原料辞典検索/diethylamino-hydroxybenzoyl-hexyl-benzoate/DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE
Tier 1 Monograph · SSOT 15 FieldsRaw .md (GEO) ↗
合成 (Synthetic)

DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE

標準 INCI 準拠: DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE
紫外線防御剤(UVフィルター)光安定化剤
[EU CosIng Official Definition] Diethylamino Hydroxybenzoyl Hexyl Benzoate is the organic compound that conforms to the formula:
結論先行 エグゼクティブ規制・安全性ファクトボックスAEO / GEO CITATION ANCHOR

化粧品における DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE のグローバル配合基準と処方特性とは?

DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE(CAS番号: 302776-68-7)は、化粧品処方において主に紫外線防御剤(UVフィルター), 光安定化剤として配合される原料です。日本厚労省/JCIA(配合制限)、韓国MFDS(配合制限)、欧州CosIng(配合制限)など6大法域の法定基準下で管理され、通常 1–10%(適正安定域 pH 4–8)で処方されます。

7大トラック 国別・用途別 公式全成分表示名称マトリクス

各国公的告示原典のみ収録 · 機械翻訳・任意音訳ゼロ
7-Track Official Statutory Label Names for DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE
法域・規制トラック公式全成分表示名称ワンクリックコピー
① 韓国 (MFDS 化粧品標準名称)DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE (KR MFDS Registered)
② 韓国旧名称履歴 (301 リダイレクト)——
③ 欧州連合 (EU CosIng EC 1223/2009)DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE
④ 米国一般化粧品 (US PCPC / MoCRA INCI)DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE
⑤ 米国 FDA OTC モノグラフ有効成分名DHHB (UNAPPROVED OTC IN US)
⑥ 中国 (NMPA IECIC 標準中国語名称)二乙氨羟苯甲酰基苯甲酸己酯
⑦ 日本化粧品表示名称 / 医薬部外品外原規名称 (JCIA / MHLW)DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE (標準INCI参照 · 任意カタカナ音訳排除)

Layer 1 — 6大法域 法定配合上限および規制ステータス

Layer 1 Statutory Regulatory Limits Across 6 Regions for DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE
法域規制ステータス配合上限制限条件および一次法源出典
韓国 (MFDS)配合制限GMP公的化粧品原料目録収載 (GMP基準内使用)
欧州 (EU)配合制限GMP公的化粧品原料目録収載 (GMP基準内使用)
米国 (FDA)配合禁止GMP公的化粧品原料目録収載 (GMP基準内使用)
中国 (NMPA)配合制限GMPIECIC Entry #2217
日本 (MHLW)配合制限GMP公的化粧品原料目録収載 (GMP基準内使用)
ASEAN (ACD)配合制限GMP公的化粧品原料目録収載 (GMP基準内使用)
⚠️ 参考用案内 (免責事項): 本辞典の成分名・規制上限・処方ガイドは研究開発の参考用です。法改正の時差やデータの誤記・漏れがあり得るため、実際の処方・ラベル表示・届出前には必ず管轄当局の最新告示原文をご確認ください。本情報の利用により生じた問題について運営主体は法的責任を負いません。
Interactive Quartile Box-Plot (Min–Q1–Median–Q3–Max)

Layer 3 Formulation Concentration Box-Plot vs. Statutory Limit

Sunscreen / Colorn=22
Min 1% · Q1 3% · Median 5% · Q3 6% · Max 10%
Sunscreen / Color — Sun care & color cosmetics dispersion / sensory modifier
Verified Source: Global Starter Formulation Library Statistical Distribution (n=22, EVONIK 22) (cir_safety) · EVONIK 22
Typical Median: 5%

Layer 3 — 剤形別通常配合濃度 (四分位数 n≥5) & 物理化学・相溶性ガイド

Layer 3 Formulation Concentration Quartiles by Product Category for DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE
剤形グループMin – Q1 – Median – Q3 – Max (%)処方役割・作用機序Source ID
剤形群 D — 日焼け止め (UV)・メイクアップ・ファンデーション1% · 3% · 5% · 6% · 10%Sun care & color cosmetics dispersion / sensory modifierGlobal Starter Formulation Library Statistical Distribution (n=22, EVONIK 22)
Cutaneous Permeation Science (500 Dalton Rule)MW: Macro/Complex · LogP: N/A

Stratum Corneum Penetration Depth & Bio-Spicule Transdermal Delivery

Stratum Corneum (Brick & Mortar Barrier · 10–20 µm)500 Da Molecular Weight Cutoff BarrierViable Epidermis (Keratinocytes & Melanocytes · 50–100 µm)Target for Brightening (Tyrosinase/Melanosome) & Barrier LipidsPapillary Dermis (Fibroblasts & ECM Collagen · 150–300 µm)Target for Collagen I/III Synthesis, Peptides, PDRN & ExosomesEpidermal Passive Permeation (<500 Da)
Molecular Weight & LogP Permeation Diagnosis
Low Molecular Weight (320 Da ≤ 500 Da) — Passive Permeation Feasible

Under passive topical application, molecules diffuse tortuously through intercellular lipids. Hydrophilic compounds >500 Da remain primarily on the outer stratum corneum.

Estimated Target Depth
40–90 µm
Optimal Delivery System
Polyol Enhancer / Serum
Colloid Interface, pH Spectrum & Thermal Stability

pH Stability Window (0–14), Thermal Limit & HLB Colloidal Phase Behavior

Water or glycol phase soluble/dispersible
Optimal Formulation pH Stability Window (0–14)pH 4.0 – 8.0
0245.5791114

Outside pH 4–8, risk of hydrolysis, viscosity loss, or ionic dissociation increases.

Maximum Thermal Processing Limit (°C)≤ 50°C
25°C45°C60°C75°C85°C100°C

Thermally stable up to 50°C during standard emulsification.

HLB Scale (0–20) & Colloidal Micelle / Lamellar Phase Simulator
O/W Oil-in-Water Micelle Emulsion (Lotion / Cream)
HLB 11.5
W/O (3–6)Lamellar (8–10.5)O/W Emulsion (11–15)Solubilizer (15–19)O/W Droplet
Biochemical Signaling & Mechanism Pathway

Cellular & Molecular Target Mechanism Flow

1. Epidermal Interaction→ Upregulation / Activation
Intercellular Lipid & Hydration Matrix
→
TEWL Reduction & Barrier Conditioning
2. Homeostasis Modulation⊣ Inhibition / Blockade
Oxidative Stress (ROS) & Irritant Cascade
⊣
Cutaneous Soothing & Homeostasis
Formulation Ontology Radial Graph

Interactive Synergy Pairings (Solid) & Incompatibility Warnings (Dashed)

+ GLYCERIN+ CAPRYLIC/CAPRIC TR…+ TOCOPHEROL✕ Verify phase compati…DIETHYLAMINO HYDRO…
Interactive Node Guide

Click any green synergy node to jump directly to its monograph, or click a red dashed node to inspect the chemical incompatibility mechanism.

代表商品名参考 (商標法第90条第1項第2号 記述的表示)
DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE

商品名は研究者がグレードを識別するための参考表記であり、各商標権は原メーカーに帰属します。

学術・毒性・処方統合モノグラフ

Tier 1 Synthesis

本原料に紐づく NIH PubMed 査読付き論文アブストラクトおよび公的毒性評価報告書のみに基づいて作成された学術要約です。

■ [1. Chemical Identity & International Labeling Nomenclature] - INCI Name: DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE | CAS No.: 302776-68-7 | EC No.: 443-860-6 - Origin: SYNTHETIC | Functions: , - Physicochemical Profile: Formula | MW /(Polymer/Complex) | / | Ionic Nature: non-ionic | CosIng/MFDS - Official Regional Label Names: US [DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE] · EU [DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE] · CN [二乙氨羟苯甲酰基苯甲酸己酯] · JP [-] · JP Quasi-Drug [-] ■ [2. Dermatological Mechanism of Action & Functional Role] - Diethylamino Hydroxybenzoyl Hexyl Benzoate is the organic compound that conforms to the formula: Classified under origin 'synthetic', it acts within the cosmetic vehicle or stratum corneum to deliver , performance and structural formulation stability. ■ [3. Global 6-Jurisdiction Regulatory Status & Safety Limits (Layer 1 & Layer 2)] - Regional Summary: KR: RESTRICTED | EU: RESTRICTED | US: BANNED | CN: RESTRICTED | JP: RESTRICTED | ASEAN: RESTRICTED (CN IECIC (2025) Entry No. 2217 (二乙氨羟苯甲酰基苯甲酸己酯)) - [CN / COMPOSITION / limited] (Max 10%): - [KR / COMPOSITION / limited] (Max 10%): - [CN / COMPOSITION / limited] (Max 10%): - Official Safety & Historical Use Concentration (Layer 2): Quantum satis (QS) within standard cosmetic safety margins ■ [4. Formulation Dosage Guide by Product Category (Layer 3-A)] - [sun_color] Typical range: 1.0 ~ 10.0% (Median 5.0%, Ref: Global Starter Formulation Library Statistical Distribution (n=22, EVONIK 22)) — Sun care & color cosmetics dispersion / sensory modifier ■ [5. Formulation Engineering, Stability & Incompatibility Matrix (Layer 3-B)] - Addition Phase: Water Phase or Cool-down Phase (< 45°C) - Optimal pH Range: pH 4.0 ~ 8.0 | Max Process Temp: Max 50°C | Electrolyte Tolerance: MEDIUM - Incompatibility / Caution: Verify phase compatibility under extreme pH or high electrolyte loads - Synergy Pairings: GLYCERIN, CAPRYLIC/CAPRIC TRIGLYCERIDE, TOCOPHEROL | Reference Trade Names: DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE ■ [6. Peer-Reviewed Literature & Official Compendia Evidence] - PMID 42197211 (2026, Molecules): Organic Sunscreens-Biological Activity from an Enzymatic Perspective - PMID 41967699 (2026, J Invest Dermatol): M10, a bioadhesive UV filter with enhanced and long-lasting photoprotection - PMID 41411795 (2026, Ecotoxicol Environ Saf): Acute toxicity of novel triazine-based UV filters towards Chlorella vulgaris and Daphnia magna: Single and mixture effec

関連査読付き学術論文 (NIH PubMed) (12)

Organic Sunscreens-Biological Activity from an Enzymatic Perspective [PMID: 42197211 · 2026]
Soba&#x144;ska AW, Soba&#x144;ski AM, Brzezi&#x144;ska E · Molecules (2026)

Selected organic sunscreens from different chemical families were investigated in the context of their ability to inhibit butyrylcholinesterase using novel Multiple Linear Regression, Artificial Neural Network, and Support Vector Regression models based on a set of six independent variables commonly associated with compounds' absorption and distribution properties. It was established that the descriptors that have a particularly strong, positive influence on the ability of compounds to inhibit BChE expressed as p IC 50 are the count of rotatable bonds ( nRot ) and lipophilicity (log D ); p IC 50 is negatively correlated with flexibility ( Flex ), fraction of sp 3 carbon atoms ( F sp3 ), caco-2 permeability ( caco2 ), and plasma protein binding ability ( PPB ). The sunscreens that are likely to be particularly strong BChE inhibitors are Ethylhexyl Triazone (ET), Diethylhexyl Butamido Triazone (DOBT), Octocrylene (OCR), and Diethylamino Hydroxybenzoyl Hexyl Benzoate (DHHB). However, it must be stressed that ET and DOBT lie outside the chemical space of the reference compounds, so predictions for these two compounds should be treated with caution.

M10, a bioadhesive UV filter with enhanced and long-lasting photoprotection [PMID: 41967699 · 2026]
Bertrand J, Aini&#xe9; L, Kim SR, S&#xe9;journ&#xe9; N, Dupont A, Makrerougras M, Kessaci M, Studenski L, Rault I, Leffell DJ, Canolle B · J Invest Dermatol (2026)
Acute toxicity of novel triazine-based UV filters towards Chlorella vulgaris and Daphnia magna: Single and mixture effect [PMID: 41411795 · 2026]
Chen R, Gao H, Wang Z, Zeng C, Liu J, Chen R · Ecotoxicol Environ Saf (2026)

The increasing utilization of novel triazine-based UV filters (UVFs) has drawn significant attention regarding their potential toxicity to aquatic organisms. However, there is limited toxicity data for these emerging UVFs. Herein, we evaluated acute toxicities of triazine-based UVFs including bis-ethylhexyloxyphenol methoxyphenol triazine (BEMT), diethylhexyl butamido triazone (DBT), and ethylhexyl triazone (EHT), towards Chlorella vulgaris and Daphnia magna. For comparison, the acute toxicities of three commonly used non-triazine-based UVFs, namely diethylamino hydroxybenzoyl hexyl benzoate (DHHB), avobenzone (AVB), and octocrylene (OCR) were also assessed. Simultaneously, we investigated the acute mixture toxicity of these compounds on Daphnia. Under single-compound exposure (&#x2264;15&#x202f;mg/L), BEMT, DBT, and EHT demonstrated less than 10&#x202f;% growth inhibition in Chlorella. In contrast, DHHB, AVB, and OCR exhibited concentration-dependent inhibition. Based on 48-hours EC 50 values for Daphnia, the triazine-based UVFs were markedly less toxic than the non-triazine counterparts. Mixture exposure experiments revealed an antagonistic effect for combinations such as BEMT+EHT, BEMT+EHT+DHHB, and DHHB+EHT, whereas the mixture&#xa0;AVB&#xa0;+&#x202f;OCR+&#x202f;BEMT exhibited primarily synergistic effects, likely attributed to distinct modes of action among its components. This study suggests that triazine-based UVFs exhibit lower acute toxicity under the conditions tested to Chlorella growth inhibition and Daphnia immobilization than the conventional non-triazine UVFs tested, providing essential data for the environmental risk assessment of these emerging contaminants.

New alternatives in photoprotection: Preparation and evaluation of lamellar silicate derivatives and their use as sunscreens [PMID: 40931463 · 2026]
Kibwila DM, Simon A, de Abreu LCL, Rodrigues CR, de Sousa VP, de P&#xe1;dula M, Cabral LM · Int J Cosmet Sci (2026)

The objective of this work is to investigate different sunscreens and Viscogel group organoclays for the preparation of new intercalated sunscreens to improve the effectiveness and safety in photoprotection using new approach methodology (NAMs). For this study, we examined Diethylamino hydroxybenzoyl hexyl benzoate (DHHB), octyl methoxycinnamate (OMC), Bemotrizinol (BEMT) and Viscogel S4&#xae;, S7&#xae;, and B8&#xae; using a set of Saccharomyces cerevisiae mutant strains that are sensitive to UVA, UVB and Solar Simulated Light (SSL) to evaluate their photoprotective and mutagenic potential. Additionally, we developed delaminated nanocomposites by chemical intercalation reactions followed by ultrasonic treatment to enhance clay exfoliation. These nanocomposites were then characterized using X-ray Powder Diffraction (XRPD), Differential Scanning Calorimetry (DSC), Thermogravimetric Analysis (TGA) and Dynamic Light Scattering (DLS). As a function of photoprotective action and safety, the combination of Viscogel S4&#xae; and OMC filter was chosen for nanocomposite development. Our results evidenced the intercalation of the OMC in the organoclay (S4&#x2009;+&#x2009;OMC-NC). Survival and mutagenesis tests indicated a positive effect of the formulation, as it increased cell survival to SSL, even without reducing mutagenesis, while its respective physical mixture was unable to provide antimutagenic protection. S4&#x2009;+&#x2009;OMC-NC showed promising results for photoprotection, offering cellular protection combined with antimutagenic effects upon SSL exposure. This formulation enables prospects for the preparation of new, effective and safe photoprotective formulations. L'objectif de ce travail de recherche est d'&#xe9;tudier diff&#xe9;rents &#xe9;crans solaires et organo&#x2010;argiles du groupe Viscogel pour la pr&#xe9;paration de nouveaux &#xe9;crans solaires intercal&#xe9;s, afin d'am&#xe9;liorer l'efficacit&#xe9; et la s&#xe9;curit&#xe9; de la photoprotection &#xe0; l'aide d'une nouvelle approche m&#xe9;thodologique (NAM). M&#xc9;THODES: Pour cette &#xe9;tude, nous avons examin&#xe9; le benzoate d'hexyle hydroxybenzoyle di&#xe9;thylamino (DHHB), le m&#xe9;thoxycinnamate d'octyle (OMC), le b&#xe9;motrizinol (BEMT), et le Viscogel S4&#xae;, S7&#xae; et B8&#xae; &#xe0; l'aide d'un ensemble de souches mutantes S.&#x2009;cerevisiae sensibles aux UVA, UVB et &#xe0; la lumi&#xe8;re simul&#xe9;e (Solar Simulated Light, SSL), afin d'&#xe9;valuer leur potentiel photoprotecteur et mutag&#xe8;ne. De plus, nous avons d&#xe9;velopp&#xe9; des nanocomposites d&#xe9;lamin&#xe9;s par des r&#xe9;actions d'intercalation chimique suivies d'un traitement par ultrasons pour am&#xe9;liorer l'exfoliation de l'argile. Ces nanocomposites ont ensuite &#xe9;t&#xe9; caract&#xe9;ris&#xe9;s &#xe0; l'aide de la diffraction des rayons X sur poudre (X&#x2010;ray Powder Diffraction, XRPD), de la calorim&#xe9;trie &#xe0; balayage diff&#xe9;rentiel (Differential Scanning Calorimetry, DSC), de l'analyse thermogravim&#xe9;trique (Thermogravimetric Analysis, TGA) et de la diffusion dynamique de la lumi&#xe8;re (Dynamic Light Scattering, DLS). R&#xc9;SULTATS: En fonction de l'action photoprotectrice et de la s&#xe9;curit&#xe9;, l'association du filtre Viscogel S4&#xae; et de l'OMC a &#xe9;t&#xe9; choisie pour le d&#xe9;veloppement des nanocomposites. Nos r&#xe9;sultats ont mis en &#xe9;vidence l'intercalation de l'OMC dans l'organo&#x2010;argile (S4&#x2009;+&#x2009;OMC NC). Les tests de survie et de mutagen&#xe8;se ont indiqu&#xe9; un effet positif de la formulation, car elle augmentait la survie cellulaire &#xe0; la SSL, sans pour autant r&#xe9;duire la mutagen&#xe8;se, tandis que son m&#xe9;lange physique respectif n'&#xe9;tait pas en mesure de fournir une protection antimutag&#xe8;ne. S4&#x2009;+&#x2009;OMC NC a montr&#xe9; des r&#xe9;sultats prometteurs pour la photoprotection, offrant une protection cellulaire associ&#xe9;e &#xe0; des effets antimutag&#xe8;nes lo

Marine sediments microbes degrade a limited repertoire of organic UV filters [PMID: 40782226 · 2025]
Fagervold SK, Roh&#xe9;e C, Lebaron P · Environ Sci Pollut Res Int (2025)

Understanding the processes that organic UV filters undergo in coastal and marine environments is crucial for assessing their long-term environmental risks. One key process is degradation by microorganisms in sediments. This study aimed to determine whether coastal marine sediments harbor microorganisms capable of degrading organic UV filters. Sediment from Toulon Harbor was tested for its degradation potential with respect to 12 different organic UV filters. Sediment microcosms showed degradation activity towards benzophenone-3 (BP3), 2-ethylhexyl salicylate (ES), and homosalate (HS) after 12&#xa0;days. However, no degradation was observed for butyl methoxydibenzoylmethane (BM), octocrylene (OC), diethylamino hydroxybenzoyl hexyl benzoate (DHHB), drometrizole trisiloxane (DTS), phenylene bis-diphenyltriazine (TriAsorB), bis-ethylhexyloxyphenol methoxyphenyl triazine (BEMT), methylene bis-benzotriazolyl tetramethylbutylphenol (MBBT), diethylhexyl butamido triazone (DBT), or ethylhexyl triazone (ET), even after 100&#xa0;days of incubation. Two degrading strains were isolated from the microcosms: a Rhodococcus strain degrading ES and a Microbacterium strain capable of degrading HS. Despite substantial efforts, the microorganism thought to be responsible for BP3 degradation could not be isolated. This work demonstrates that microorganisms in coastal sediments can degrade a limited range of organic UV filters.

Assessing the exposure to the UV filter DHHB in urine samples from the German Environmental Specimen Bank (2000-2021): Evaluating the impact of a potential impurity of di-n-hexyl phthalate in DHHB [PMID: 40117958 · 2025]
Scherer M, Scherer G, Riedel K, Koch HM, Wrobel SA, Murawski A, Lemke N, Weber T, Pluym N, Kolossa-Gehring M · Int J Hyg Environ Health (2025)

Human biomonitoring (HBM) has become a crucial tool for assessing exposure to emerging chemicals. We analyzed 250 24-h urine samples from the German Environmental Specimen Bank (ESB), collected between 2000 and 2021, for exposure to diethylamino hydroxybenzoyl hexyl benzoate (DHHB), a UV filter increasingly used in sunscreens. Three major metabolites were examined: 2-(4-diethylamino)-, 2-(4-ethylamino)-, and 2-(4-amino)-2-hydroxybenzoyl)benzoic acid (DHB, EHB, AHB), with detection rates of 18&#xb0;%, 13&#xb0;%, and 87&#xb0;%, respectively. While EHB and DHB were specific to DHHB, AHB suggested other exposure sources, making it unreliable for assessing DHHB exposure. DHB and EHB were first detected in 2012, with increased detection rates thereafter. The median daily intake of 37&#xa0;ng/kg bw/d was much lower than the derived no-effect level of 2900&#xa0;mg/kg bw/d, indicating low risk from DHHB exposure. However, since the analyzed ESB samples were collected in winter, they likely reflect exposure from other products and the environment rather than sunscreen-related exposure. Recently, concerns have emerged regarding the DHHB impurity di-n-hexylphthalate (DnHexP), a reproductive toxicant not authorized in the EU. Retrospective analysis of oral DHHB dosing experiments indeed revealed impurity related dose-dependent excretion of DnHexP metabolites (MnHexP, oxidized 5-OH-MnHexP, and 5-oxo-MnHexP). Due to uncertainties in dose allocation, only a rough excretion fraction of 45&#xb0;% for MnHexP was derived. Our findings suggest that the DHHB impurity DnHexP may contribute to DnHexP exposure in sunscreen users applying products with contaminated DHHB. Given DnHexP's toxicity, this warrants re-assessment of DHHB's safety in cosmetics and enhanced surveillance of both DHHB and DnHexP in HBM studies.

Use of Propolis and Echinacea extracts as alternatives to organic filter in photoprotective formulations [PMID: 39853158 · 2026]
Giannakopoulou G, Pavlou P, Papageorgiou S, Siamidi A, Vlachou M, Varvaresou A · Nat Prod Res (2026)

Recently, the cosmetic and pharmaceutical industries have aimed to reduce the concentration of EU-approved organic filters in their products by incorporating more natural ingredients. The goal is to find effective SPF boosters from plants while maintaining high protection levels and adhering to ecological and public health standards. This study focuses on developing a sunscreen formulation that replaces the organic filter EHMC (2-ethylhexyl-4-meth-oxycinnamate) with extracts from Echinacea purpurea and/or Propolis oil. The new formulation, which includes Ethylhexyltriazone (EHT), Octocrylene (OCR), Diethylamino hydroxybenzoyl hexyl benzoate (DHHB), and Methylene bis -benzotriazol-yltetramethylbutylphenol (MBBT), was compared with a control formulation containing EHMC. The results showed that the plant-based combination significantly enhanced the in vitro SPF and UVAPF by over 80% and 60%, respectively.

Targeted and untargeted discovery of UV filters and emerging contaminants with environmental risk assessment on the Northwestern Mediterranean coast [PMID: 39824136 · 2025]
Gandar A, Giraudo M, Perion T, Hou&#xeb;l E, Noguer T, Rodrigues AMS, Calas-Blanchard C, Stien D · Mar Pollut Bull (2025)

Marine ecosystems, particularly coastal areas, are becoming increasingly vulnerable to pollution from human activities. Persistent organic pollutants and contaminants of emerging concern (CECs) are recognized as significant threats to both human and environmental health. Our study aimed to identify the molecules present in the seawater of two bathing areas in the Western Mediterranean Sea. Polar Organic Chemical Integrative Samplers were employed for passive sampling of UV filters and other contaminants in the seawater. The concentrations of UV filters bemotrizinol (BEMT), benzophenone-3 (BP3), diethylamino hydroxybenzoyl hexyl benzoate (DHHB), octyl triazone (ET), and octocrylene (OC) were measured at these bathing sites during the summer of 2022. In addition, non-targeted chemical analysis was used to complement the list of pollutants in the sampling areas, leading to the identification of 53 contaminants and three natural products. Dodecyltrimethylammonium (DTA) and tetradecyltrimethylammonium (TTA) ions, 1,3-diphenylguanidine (DPG), N,N-diethyl-m-toluamide (DEET), and crystal violet (CV) were successfully quantified. Risk assessments showed that DEET, DPG, and BP3 present low environmental risks at the detected concentrations, while CV, DTA, and TTA pose medium to high risks, warranting further investigation. OC was found to pose a significant risk to marine biodiversity, as its environmental concentrations exceeded predicted no-effect concentration values. Overall, this study highlights the complexity of environmental pollution in coastal bathing areas and underscores the urgent need for comprehensive risk assessments to safeguard marine life and public health.

Organic Sunscreens and Their Products of Degradation in Biotic and Abiotic Conditions-In Silico Studies of Drug-Likeness and Human Placental Transport [PMID: 39596438 · 2024]
Soba&#x144;ska AW, Banerjee A, Roy K · Int J Mol Sci (2024)

A total of 16 organic sunscreens and over 160 products of their degradation in biotic and abiotic conditions were investigated in the context of their safety during pregnancy. Drug-likeness and the ability of the studied compounds to be absorbed from the gastrointestinal tract and cross the human placenta were predicted in silico using the SwissADME software (for drug-likeness and oral absorption) and multiple linear regression and "ARKA" models (for placenta permeability expressed as fetus-to-mother blood concentration in the state of equilibrium), with the latter outperforming the MLR models. It was established that most of the studied compounds can be absorbed from the gastrointestinal tract. The drug-likeness of the studied compounds (expressed as a binary descriptor, Lipinski ) is closely related to their ability to cross the placenta (most likely by a passive diffusion mechanism). The organic sunscreens and their degradation products are likely to cross the placenta, except for very bulky and highly lipophilic 1,3,5-triazine derivatives; an avobenzone degradation product, 1,2-bis(4-tert-butylphenyl)ethane-1,2-dione; diethylamino hydroxybenzoyl hexyl benzoate; and dimerization products of sunscreens from the 4-methoxycinnamate group.

Inorganic UV filter-based sunscreens labelled as eco-friendly threaten sea urchin populations [PMID: 38703981 · 2024]
Marcellini F, Varrella S, Ghilardi M, Barucca G, Giorgetti A, Danovaro R, Corinaldesi C · Environ Pollut (2024)

Although the negative effects of inorganic UV filters have been documented on several marine organisms, sunscreen products containing such filters are available in the market and proposed as eco-friendly substitutes for harmful, and already banned, organic UV filters (e.g. octinoxate and oxybenzone). In the present study, we investigated the effects of four sunscreen products, labelled by cosmetic companies as "eco-friendly", on the early developmental stages of the sea urchin Paracentrotus lividus, a keystone species occurring in vulnerable coastal habitats. Among sunscreens tested, those containing ZnO and TiO 2 or their mix caused severe impacts on sea urchin embryos. We show that inorganic UV filters were incorporated by larvae during their development and, despite the activation of defence strategies (e.g. phagocytosis by coelomocytes), generated anomalies such as skeletal malformations and tissue necrosis. Conversely, the sunscreen product containing only new-generation organic UV filters (e.g. methylene bis-benzotriazolyl tetramethyl, ethylhexyl triazone, butylphenol diethylamino hydroxybenzoyl hexyl benzoate) did not affect sea urchins, thus resulting actually eco-compatible. Our findings expand information on the impact of inorganic UV filters on marine life, corroborate the need to improve the eco-friendliness assessment of sunscreen products and warn of the risk of bioaccumulation and potential biomagnification of inorganic UV filters along the marine food chain.

Microbial consortia degrade several widely used organic UV filters, but a number of hydrophobic filters remain recalcitrant to biodegradation [PMID: 38010544 · 2023]
Fagervold SK, Roh&#xe9;e C, Lebaron P · Environ Sci Pollut Res Int (2023)

Organic UV filters are important ingredients in many personal care products, including sunscreens. Evaluating the biodegradability of organic UV filters is key to estimate their recalcitrance and environmental fate and thus central to their overall environmental risk assessment. In order to further understand the degradation process, the aim was to investigate whether specific consortia could degrade certain UV filters. Several bacterial strains were isolated from enrichment cultures actively degrading octocrylene (OC), butyl methoxydibenzoylmethane (BM), homosalate (HS), and 2-ethylhexyl salicylate (ES) and were utilized to construct an in-house consortium. This synthetic consortium contained 27 bacterial strains and degraded OC, BM, HS, and ES 60-80% after 12&#xa0;days, but not benzophenone-3 (BP3), methoxyphenyl triazine (BEMT), methylene bis-benzotriazolyl tetramethylbutylphenol (MBBT), diethylhexyl butamido triazone (DBT), ethylhexyl triazone (EHT), or diethylamino hydroxybenzoyl hexyl benzoate (DHHB). Furthermore, several commercial microbial mixtures from Greencell were tested to assess their degradation activity toward the same organic UV filters. ES and HS were degraded by some of the commercial consortia, but to a lesser extent. The rest of the tested UV filters were not degraded by any of the commercial bacterial mixes. These results confirm that some organic UV filters are recalcitrant to biodegradation, while others are degraded by a specific set of microorganisms.

Sunscreens [PMID: 41730063 · 2006]
Unknown Authors · PubMed Journal (2006)

よくある質問 (FAQ)

Q1. DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE の各国公式全成分表示名称(7トラック)はどのように異なりますか?
日本化粧品工業連合会(JCIA)表示名称は 'DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE (標準INCI準拠)'、米国PCPC・欧州CosIng INCIは 'DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE'、中国NMPA IECIC標準中国語名は '二乙氨羟苯甲酰基苯甲酸己酯' です。
Q2. DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE のグローバル6大法域における法定配合基準 (Layer 1) は?
6大法域規制ステータス — 日本(JP): restricted、韓国(KR): restricted、欧州(EU): restricted、米国(US): banned、中国(CN): restricted、ASEAN: restricted。
Q3. 処方設計における DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE の通常配合濃度 (Layer 3) と適正 pH は?
主要剤形 (sun_color) において通常 1〜10%(中央値 5%)で配合され、適正pH範囲は 4〜8 です。
Q4. DIETHYLAMINO HYDROXYBENZOYL HEXYL BENZOATE の配合禁忌 (Incompatibilities) と推奨シナジー成分は?
推奨シナジーペアは GLYCERIN, CAPRYLIC/CAPRIC TRIGLYCERIDE, TOCOPHEROL、配合上の注意点は Verify phase compatibility under extreme pH or high electrolyte loads です。